Using the methane for cooking
IRRI Mexico
Lots of methane gas production harnessed for use and removal from atmosphere
Effluent from biodigester

Testing biodigester effluent is also important in order to know how effective it is as a fertilizer. Many farmers rely on manure from their animals and biodigesters take this animal manure to produce gas. Making sure the resulting biodigester effluent can also be used as a fertilizer with equal or better results to that of traditional or commonly used fertilizers is extremely important to insuring that the biodigester can become an integrated addition to the farm.

Background

Testing is being done by the Laboratorio de Ajusco de Tecnologia Alternativa, a nonprofit laboratory providing technical assistance in testing different appropriate technologies. Right now they are working with Isla Urbana for rainwater quality testing and the International Renewable Resources Institute-Mexico for biodigester effluence water and fertilizer quality studies.

The International Renewable Resources Institute and Biobolsa wanted to test their biodidgester systems for fertilizer quality and applicability. This is part of a testing series for biodigester effluence the accompanying testing is on water quality of biodigesters.

Fertilizer Quality Expectations

Soil Basics

Parameters List

Macro Nutrients Micro nutrients
Nitrogen, N Iron
Phosphorous, Ph Maganese
Potassium, K Boron
Calcium, Ca Copper
Magnesium, Mg Zinc
Sulphur, S Molybdenum

Different Nutrients and Their Functions for Plants

6 Macro Elements

Macro Nutrient Concentration Limits

Nutrient Removed in soil (kg/ha) Available in Soil (kg/ha) Insoluble (kg/ha)
Nitrogen, N 100 20-200 1,000- 10,000
Phosphorous, Ph 20 20-200 1,000- 10,000
Potassium, K 100 40-200 5,000-50,000
Calcium, Ca 40 100-5000 10,000-100,000
Magnesium, Mg 20 100-1000 2,000-100,000
Sulphur, S 30 50-100 100-10,000

[6]

1.Nitrogen (N)

' Bioavailable Nitrogen

Nitrate, NO3-
Ammonium, NH4+

Nitrate, NO3-

dentrification or nitrification.[10]

The general limits of nitrates from leafy vegetables and drinking water is 100-170 mg/day of human consumption.[14]

Nitrite, NO2

Nitrite is not bio available, but must be converted into nitrate for use by plants. Small concentrations of nitrite can be toxic to plants, but nitrite is an important intermediate in the conversion of ammonium to nitrate in the soil. Nitrite is also formed by dentrification, or the bacterial reduction of nitrate to nitrite, this occurs under anoxic (or oxygen deprived) conditions. Nitrite is not a stable intermediate and very few cases of nitrite accumulation have been reported. The levels of nitrite usually do not exceed 0.25 to 70 ppm within soil. Accumulation however can occur in neutral or alkaline soils, since the conversion from nitrite to nitrate is inhibited more than the conversion of ammonia to nitrite.[15] Also bacteria present in sewage sludge converts nitrates into nitrites.[16]

Ammonia, NH3

Ammonia is not bio available but must be converted into Ammonium for uptake by plants. This is very volatile and needs to be transformed into other forms of nitrogen like urea for storage. Ammonia is the pungent smell from composts with too much nitrogen and not enough carbon. Ammonia is also the form of nitrogen most commonly converted into synthetic nitrogen compounds, like nitric acid, for industrial fertilizer applications.

Ammonium, NH4+

Ammonium is just as available to plants as nitrate, however ammonium usually does not accumulate into the soil because it readily is converted to nitrate in most conditions.[17] Ammonium is less able to leach from the soil, however it is very volatile and can easily escape in aerobic environments.[18] Ammonium can be toxic in high enough concentrations and for this reason plants usually do not readily uptake this as readily as nitrate.

Organic nitrogen

Total Kjeldahl Nitrogen (TKN)

Total Kjeldahl Nitrogen is the sum of organic nitrogen, ammonia (NH3), and ammonium (NH4+).

Total Nitrogen

Total Nitrogen can be derived by finding total kjeldahl nitrogen (TKN), ammonia, and nitrate-nitrite and adding them together. Total Nitrogen does not include N2, which is not bioavailable.[21]

2.Phosphorous (Ph)

Phosphate Phosphorous Is concentrated in soils by manures from seed eating birds.

Potash Phosphorous

Is concentrated in soils by burnt and rotted plants or composts.

3.Potassium (K)

Nitrogen, Potassium, and Phosphorous values for different Fruits and Veggies

Fruits and Veggies (to produce 1 tonne) Needed Nitrogen Needed Potassium Needed Phosphorous
Tomato * 2.5 to 3 kg .2 to.3 kg 3 to 3.5 kg
Eggplant * 3 to 3.5 kg .2 to.3 kg 2.5 to 3 kg
Chili and Bell Peppers * 3 to 3.5 kg .8 to 1 kg 5 to 6 kg

4.Calcium (Ca)

5.Magnesium (Mg)

6.Sulphur (S)

6 Micro Elements

Concentration Limit for Micro Elements in Waste Water Agricultural Application

Nutrient upper limit (mg/l)
Iron 5.0
Maganese .20
Boron 3.0
Copper .20
Zinc 2.0
Molybdenum, Mo .01

[34]

Concentration Limit and Availability in Soil

Nutrient Removed in soil (kg/ha) Available in Soil (kg/ha) Insoluble (kg/ha)
Iron, Fe .5 10-200 2,000-100,000
Boron, Bo 3.0 1-5 4-100
Copper .1 1-20 2- 200
Zinc .2 2-200 100- 100,000
Molybdenum, Mb .01 .002-1.0 .5-10

[35]

Balancing Proportions between Major Ions in Soil

Major Ions in Soil Proportion Notes
Calcium, Ca 50
Magnesium 35 add Epsom salt or dolomite if Mg deficient
Potassium, K 6 adding K increases Na
Sodium, Na 5 Na displaces Ca

[36]

1.Iron

2.Maganese

3.Boron

4.Copper

5.Zinc

6.Molybdenum

Other Parameters for Concern in Waste Water Agriculture Application

Expected Parameter Concentrations of Influent and Effluent Water Quality from Biodigester

Parameter Mean Range
ph of influent* 6.7 6.4- 7.1
pH of effluent* 7.2 6.8 -7.5
E. Coli before loading** 52,890 11,000-150,000
E. coli of effluent** 75 2- 450

pH

The pH of soils is one of the most important properties that effects nutrient availability.

E. Coli

Testing for coliform bacteria is cheaper and a lot faster than testing for specific organisms and pathogens, thus the U.S. Public Health Service created a standard in 1914 for coliform concentration as an indicator of overall microbiological suitability of drinking and surface waters. 1 fecal coliform/ 100ml = 1 ppb = 0.001 ppm.

Sodium, Na

High concentrations of sodium ions found in waste water and used to irrigate agricultural areas reduce the infiltration rate and permeability of soils. When these soils dry a crust forms creating problems for tillage and interfering with germination and seedling emergence. These effects are dependent on the sodium ion concentration relative to the concentration of calcium and magnesium ions and the total salt concentration. Since the total salt concentrations in sewage effluent can be several hundred mg/l higher than in drinking water, total salt is an important indicator of the quality of fertilizers and irrigation waters from sewage.[38] SAR, Sodium adsorption ratio.

Soil Structure

Soil structure (whether porous or compacted) effects the soil's permeability, susceptibility to erosion, root growth, and the ability of soil to retain nutrients. While synthetic fertilizers fail to renew and rebuild soil structure, composted manures and foods scraps have the ability to add to and renew the soil structure. The structure depends on the soil composition of sand, silt, clay, and organic matter in the soil as well as the presence of any flocculating or ionic substances.[39]

The soil structure can be qualitatively analyzed by just visually and physically feeling the texture of the soil. Another test for soil structure can be done by placing a soil sample in a tall mason jar filled with water and after shaking vigorously allow the particles to settle out over a day. The different components will stratify, with gravel ans sand falling to the bottom, silt above that, clay above that, organic particles above that, and just water at the top clear area. Testing biol's ability to build up soil structure is an important quality assessment.

Testing Biol Samples

Lab Testing

Field Testing

References

  1. ↑ Kevin A. Handreck and Neil D. Black. Growing media for ornamental plants and turf. UNSW Press, 2002.
  2. ↑ Dudley Harris. Hydroponics: the complete guide to gardening without soil. Struik, 1992
  3. ↑ Harris, Dudley. Hydroponics: the complete guide to gardening without soil. Struik, 1992.
  4. ↑ Kevin A. Handreck and Neil D. Black. Growing media for ornamental plants and turf. UNSW Press, 2002.
  5. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  6. ↑ Mollison, Bill. Permaculture: A Designer's Manual. Tagari, 1988. Pg 576.
  7. ↑ Food and Agriculture Organization of the United Nations, FAO. Wastewater quality guidelines for agricultural use. http://www.fao.org/docrep/t0551e/t0551e04.htm#2.3 effluent quality guidelines for health protection
  8. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  9. ↑ E. I. UWAH*, J. ABAH, N. P. NDAHI and V. O. OGUGBUAJA. CONCENTRATION LEVELS OF NITRATE AND NITRITE IN SOILS AND SOME LEAFY VEGETABLES OBTAINED IN MAIDUGURI, NIGERIA. Journal of Applied Sciences in Environmental Sanitation. University of Maiduguri. August 2009.
  10. ↑ M.L. Vitosh, Extension Specialist. N-P-K FERTILIZERS. Michigan State University Agricultural Extension Bulletin. http://web.archive.org/web/20100612165241/http://www.canr.msu.edu/vanburen/e-896.htm.
  11. ↑ U.S. Geological Survey. USGS Water Quality Information. http://water.usgs.gov/owq/FAQ.htm
  12. ↑ U.S. Geological Survey. USGS Water Quality Information. http://water.usgs.gov/owq/FAQ.htm
  13. ↑ C Kameswara Rao. Toxicity of Nitrates and Nitrites in Plants. Foundation for Biotechnology Awareness and Education. Bangalore, India. July, 2007.
  14. ↑ E. I. UWAH*, J. ABAH, N. P. NDAHI and V. O. OGUGBUAJA. CONCENTRATION LEVELS OF NITRATE AND NITRITE IN SOILS AND SOME LEAFY VEGETABLES OBTAINED IN MAIDUGURI, NIGERIA. Journal of Applied Sciences in Environmental Sanitation. University of Maiduguri. August 2009.
  15. ↑ O. L. OKE. Nitrite Toxicity to Plants. Nature Vol. 212, 528. Oct. 29,1966.
  16. ↑ Mollison, Bill. Permaculture: A Designer's Manual. Tagari, 1988. Pg 576.
  17. ↑ Camberato, Jim and Nielsen, R.L. Soil Sampling for Assessing Plant Available N Following Excessive Rain or Flooding. Purdue University, Agronomy Department. West Lafayette, IN. June 2010. http://www.agry.purdue.edu/ext/corn/news/timeless/AssessAvailableN.html
  18. ↑ Graham Merrington. Agricultural pollution: environmental problems and practical solutions. Taylor & Francis, 2002.
  19. ↑ Drangert, JO. Fighting the Urine Blindness to Provide more Sanitation Options. Water SA. Vol 24, No 2. April, 1998. http://web.archive.org/web/20141222023233/http://www2.gtz.de:80/Dokumente/oe44/ecosan/en-fighting-urine-blindness-1998.pdf
  20. ↑ M.L. Vitosh, Extension Specialist. N-P-K FERTILIZERS. Michigan State University Agricultural Extension Bulletin. http://web.archive.org/web/20100612165241/http://www.canr.msu.edu/vanburen/e-896.htm.
  21. ↑ US Environmental Protection Agency. Total Nitrogen. Tribal Water Protection. http://www.epa.gov/region9/water/tribal/pdf/cwa-reporting/Total-Nitrogen.pdf.
  22. ↑ Leo Lewis. Scientists warn of lack of vital phosphorus as biofuels raise demand. The Times. June 23, 2008.
  23. ↑ International Plant Nutrition Institute. Functions of Potassium in Plants. Better Crops with Plant Food. http://web.archive.org/web/20180831063733/https://www.ipni.net/ppiweb/bcrops.nsf/$webindex/84CBB51751971AB3852568F000673A10/$file/98-3p04.pdf
  24. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  25. ↑ Joe Traynor. Ideas in Soil and Plant Nutrition. 1980. Kovak Books, Bakersfield, CA.
  26. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  27. ↑ D.M. Hegde. Nutrient Requirements of Solanaceous Vegetable Crops. All India Coordinated Safflower Improvement Project. Food and Fertilizer Technology Center for the Asian and Pacific Region. Solapur, Maharashtra, India, 07, 1997. http://web.archive.org/web/20111122155822/http://www.agnet.org:80/library/eb/441/
  28. ↑ Greg Patterson. Calcium Nutrition in Plants. Certified Crop Advisor.
  29. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  30. ↑ Mollison, Bill. Permaculture a Designers Manual. Tagari, 1988.Pg 190- 198.
  31. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  32. ↑ H Rennenberg. The Fate of Excess Sulfur in Higher Plants. Annual Review of Plant Physiology Vol. 35: 121-153 (Volume publication date June 1984).
  33. ↑ Thomas Marler, Frank Cruz and James McConnell. Essential Plant Nutrients. College of Agriculture and Life Sciences, University of Guam
  34. ↑ Food and Agriculture Organization of the United Nations, FAO. Wastewater quality guidelines for agricultural use. http://www.fao.org/docrep/t0551e/t0551e04.htm#2.3 effluent quality guidelines for health protection
  35. ↑ Mollison, Bill. Permaculture: A Designer's Manual. Tagari, 1988. Pg 576.
  36. ↑ Mollison, Bill. Permaculture a Designers Manual. Tagari, 1988.Pg 190- 198.
  37. ↑ North Carolina Department of Agriculture and Consumer Services.Plant Nutrients. http://www.ncagr.gov/
  38. ↑ Food and Agriculture Organization of the United Nations, FAO. Wastewater quality guidelines for agricultural use. http://www.fao.org/docrep/t0551e/t0551e04.htm#2.3 effluent quality guidelines for health protection
  39. ↑ Mollison, Bill. Permaculture: A Designer's Manual. Tagari, 1988. Pg 576.
  40. ↑ Camberato, Jim and Nielsen, R.L. Soil Sampling for Assessing Plant Available N Following Excessive Rain or Flooding. Purdue University, Agronomy Department. West Lafayette, IN. June 2010. http://www.agry.purdue.edu/ext/corn/news/timeless/AssessAvailableN.html
  41. ↑ Regula Züger. Impact Assessment of Farmer Field Schools in Cajamarca, Peru: An Economic Evaluation. International Potato Center. Lima, Peru; March 2004. http://www.cipotato.org/library/pdfdocs/AN65008.pdf
Page data
Keywords Biogas, Fertilizers, Agriculture, Project testing, Anaerobic digestion
SDG SDG06 Clean water and sanitation, SDG07 Affordable and clean energy, SDG11 Sustainable cities and communities
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